Behavioral Ecology Vol. 7 No. 4: 494-500 Within-bout dynamics of diet choice Heikki Hirvonen and Esa Ranta Integrative Ecology Unit, Division of Population Biology, Department of Ecology and Systematics, PO Box 17, FIN-00014 University of Helsinki, Finland Conventional diet theories mostly ignore dynamics in prey selectivity during a foraging bout. However, results from experiments with several aquatic predator species showed that, as more prey were eaten, the predators included more of the initially less profitable (small) prey types in their diets. We also found that handling times of the initially more profitable (large) prey types increased with prey sequence, but handling times of the small prey remained constant Consequently, relative profitability of the large prey declined over the foraging trials. We modeled prey choice by incorporating the change in handling time as a function of prey sequence. The model predicts a shift in diet as the relative prey values change during a foraging period. The predictions qualitatively match the empirical data. In addition, simulations over the foraging bout showed that adopting the strategy using updated profitabilities always gives higher or at least as high total energetic gain as the fixed strategy based on the classical optimal prey-choice model. These results imply that the predators reevaluate prey profitabilities and adjust their selectivity accordingly in the course of foraging, without abandoning rate maximization. We suggest that dynamics of diet choice may in part account for partial preferences frequently observed in studies on prey selection. Key words: foraging behavior, foraging models, handling time, optimal foraging, partial preferences, prey selection, profitability. [Behav Ecol 7:494—500 (1996)] S ince the pioneering endeavors of Emlen (1966) and MacArthur and Pianka (1966), foraging theory has mosdy focused on prey and patch models. The classical model of prey choice was put forth by Schoener (1971) and Charnov (1976) (but see also Emlen, 1973; Pulliam, 1974; Werner and Hall, 1974). The model assumptions and predictions have been summarized by Krebs and McCleery (1984), Stephens and Krebs (1986), and Krebs and Kacelnik (1991: Table 1). The classical prey-choice model predicts that the more profitable prey type should always be accepted upon encounter. Further, according to the model, the inclusion of low-ranking prey should not depend on encounter rate, and the inclusion should be all or nothing. Much empirical work has been done to verify the prey model (for reviews see Krebs and Kacelnik, 1991; Stephens and Krebs, 1986), but the alk>r-none rule has not been supported by experimental results. As the classical prey model is based on Holling's disc equation (Holling, 1959), an implicit assumption is that the net energy intake per unit handling time (profitability) of a specific prey type is constant (Charnov, 1976; Krebs et al., 1983; Stephens and Krebs, 1986). Consequently, the classical preychoice model does not predict any change in diet within a patch and in the course of a foraging bout (Table 1; Krebs et al., 1983; Stephens and Krebs, 1986). However, there is some evidence that prey profitabilities change during foraging (e.g., Bindoo and Aravindan, 1992; Croy and Hughes, 1991) and that foraging animals alter their diets within a single foraging bout (e.g., Confer and O'Bryan, 1989; Godin, 1990; Lucas, 1990). The most common explanation for diet dynamics is forager satiation, but there are contradictory views about how diet should change as hunger level declines. For example, Richards (1983) suggested a model predicting expanding diet as a forager is near satiation. In contrast, Snyderman (1983) found that pigeons increased prey selectivity with decreased deprivation. According to Pulliam's formulation of the optimal preychoice model (Pulliam, 1974), the diet that maximizes the Received 7 February 1995; first revision 28 June 1995; second revision 7 December 1995; accepted 20 January 1996. 1045-2249/96/S5.00 O 1996 International Society for Behavioral Ecology rate of energy intake should be unaffected by predator satiation. However, if relative prey profitabilities change in die course of foraging, an optimally foraging animal might tend to shift its diet selection according to these changes. This could alter prey choice from that predicted by the classical diet model and would result in apparent partial preferences (McNamara and Houston, 1987). Unfortunately, most studies on prey choice report data pooled over the entire foraging period and do not provide sequential data on handling times or on diet selection. Therefore, it is impossible to determine the role of variable prey profitabilities in explaining diet dynamics from published works. Here we examine the consequences of handling time as a function of prey sequence on prey choice. We assume that a foraging bout is the total amount of uninterrupted time available for foraging in a patch of prey with no prey depletion. We first present empirical data on dynamics of diet selection by four different small aquatic predator species. Invariably, we find that diet width increases toward die end of the foraging bout and handling time for the larger prey type increases widi the number of that prey type eaten, whereas handling time for die small prey remains unchanged. This observation is then incorporated into a modified diet model assuming that the predators update prey profitability according to changes in handling times. We dien compare the performance of a forager adopting this strategy widi the performance of a forager using a fixed prey-choice strategy according to the classical prey model and die performance of a strategy based on a truly omniscient predator using a dynamic decision model. Empirical observations Dynamics of diet choice We used data on prey-size selection by larvae of two anisopteran odonate species (Aeshna juncea and Leucorrhinia dubia), die ten-spined stickleback (Pungitius pungitius), and die smooth newt (Triturus wdgaris). Diet choice was studied in experiments widi different prey types available to die predators. To eliminate the effects of prey depletion on prey selection, both prey densities and prey ratios were kept constant All animals had been deprived of food before die trials. De- 495 Hirvonen and Ranta • Diet dynamics 100 Table 1 Assumptions and predictions of the classical optimal prey-choice model (after Krebs and McCleery, 1984; Stephens and Krebs, 1986; Krebs and Kacemik, 1991) Assumptions Net energy is a valid measure of prey value Long-term average rate of energy intake is maximized Handling time is a fixed constraint Net energy gain and encounter ate for the tth prey are fixed and not functions of pt Energetic costs per unit of handling time are similar for different prey, i Handling and searching are mutually exclusive Prey type, i, is recognizable without errors Prey are encountered sequentially and randomly The expected time to find the next prey of type i is always 1/X, The forager does not use information it may acquire while foraging Predictions The highest ranking prey, maxte/Aj), should always be accepted Low-ranking prey should be ignored according to the inequality in Equation 2 The exclusion of low-ranking prey is all or nothing The exclusion of a low-ranking prey does not depend on the animal's encounter rate, \b with that prey type 60 «j- Aeshna Leucorrhinia juncea dubia 11 12 i' 20 100:200 100 0) a. E 60 I 20 c o c o Pungitius pungitius 9 T "ca 100:200 7x 10 8 iI i ist half 2nd 10:10 30:30 50:50100:100 100 QO 60 20 privation time for the odonates was 4 days, for the sticklebacks 12 h, and for the newts, 10 h on average. We conducted the dragonfly experiments in aquaria containing 1.5 1 of water. Small and large Daphnia magna (mean lengdis 2.2 mm and 3.8 mm) were offered to the larvae in constant density and ratio of 200:100. Predation events were monitored and recorded sequentially. Each trial lasted 30 min. The large prey size was initially the most profitable one and abundant enough to promote specialization on that prey (according to the threshold for specialization by the classical prey model). We reanalyzed the original data by Ranta and Nuutinen (1984), who examined prey-size (1.5 mm D. longispina and 2.3 mm D. magna) selection by ten-spined sticklebacks in 40-1 aquaria. Prey were given in 1:1 ratios in four densities (Figure 1). Trials lasting 5 min were used, and prey types eaten were scored. As Ranta and Nuutinen (1985) examined prey-size selection by adults of the smooth newt in much the same way (2-1 aquarium, 10-min trials), their data (Figure 1) were also reanalyzed. We used the original sequential data of prey captures recorded during the foraging bouts. For all the predators used in the experiments, initial prey profitability increased with prey size. We examined the performance of individual foragers in die course of the foraging trials. For the analyses, the proportion of the smaller prey in the foragers' diet was scored before and after they had eaten half of the prey (= median prey) during die experimental trial. The data were subjected to a repeatedmeasures ANOVA. During foraging, all the predators examined changed their diet choice (Figure 1), and the ANOVA showed diat in all cases the time effect (half) is significant (Table 2). Hence, the proportion of the smaller prey in the foragers' diet was higher in the second half of all prey eaten than in the first half (Figure 1). Handling time Our observations on prey handling times originate from experiments in which the predators were offered a single prey 5:25 10:2015:15 20:10 25:5 LARGE : SMALL prey Figure 1 Proportion of small prey (mean with 95% confidence limit) in the diet of four small aquatic predator species. The total number of prey eaten is split into two halves: the first half refers to small prey among the first 50% of all prey eaten, and the second half refers to small prey among the latter 50% of all prey. For the ten-spined stickleback, large and small prey were provided in different densities and for the smooth newt in different ratios (large:small). Italic numbers refer to sample sizes (for statistical tests, see Table 2). type. Prey handling times of medium-sized (instar F-2) A. juncea were measured in 30-min experiments (in an aquarium with 1.5 1 of water) by providing them in separate runs with 100 D. magna of 1.7, 2.7, and 3.8 mm. The larvae were deprived of food for 4 days before die trials. We measured handling time as die time between a capture and termination of feeding movements of the larval labium. The results clearly indicate that widi the two largest prey sizes, handling time is a function of the sequence number of the prey eaten (Figure 2), whereas with the smallest D. magna, diere is no change in handling time with successive feeds. With the ten-spined sticklebacks, the prey used were 2.3-mm D. magna and 1.5-mm D. longispina (in a 5-1 aquarium with 10 prey items). Before the experiments, die sticklebacks were deprived of food for 12 h. The handling time was measured from a successful strike until initiation of a search for a new prey item (Ranta and Nuutinen, 1984). Because Ranta and Nuutinen (1984) reported only the mean handling times, we reexamined the original sequential records of the handling times. Mean handling time of the larger fish (39 mm) for the first large prey eaten was 4.6 s (SE = 0.7), and for the sixth item in sequence handling time was 9.5 s (SE = 2.2; paired t test, *,„ = 4.82, p = .0045). The values for 23-mm fish with large prey were 16.8 s (SE = 1.8) and Behavioral Ecology Vol. 7 No. 4 496 Table 2 Univariate repeated-measures ANOVA tables of changes in diet during the foraging trials for the three different types of predators Source SS Odonates Between subjects Species 0.159 Error 2.107 Within subjects Half 0.303 Half*species 0.001 Error 0.800 Ten-spined stickleback Between subjects Density5 0.52 Error 1.27 Within subjects Half* 1.270 Half*density 0.041 Error 1.136 Smooth newt Between subjects Ratio" 3.178 Error 3.238 Within subjects Half* 0.737 Half*ratio 0.111 Error 1.537 Aeshnajuncea 100 df MS 1 21 0.159 0.100 1.585 .222 1 1 21 0.303 0.001 0.038 7.945 0.014 .010 .905 3 4.10 .015 30 . 0.17 0.04 1 3 30 1.27 0.01 0.03 33.53 0.36 .000 .779 o CD W <D r SMALL PREY, y - 17 + 0.1 x.r- 0.09 r MEDIUM PREY, y - 37+ 1.9 x.r- 0.38 • • • 100 i 0 (C) 200 4 38 0.794 0.085 9.322 .000 1 4 38 0.737 0.028 0.040 18.229 0.686 .000 .606 100 LARGE PREY, y = 93 + 8.7 x, r= 0.47 * The response variable (half) is the proportion of smaller prey (arcsine square-root transformed) in the diet among the first half and second half of prey eaten. b The subjects of density (sticklebacks) and ratio (smooth newt) are discussed elsewhere (Ranta and Nuutinen, 1984, 1985; Nuutinen and Ranta, 1986). 5 15 25 Prey sequence Figure 2 26.6 s (SE = 3.9) for the first and the sixth prey items, respectively (<12 = 2.70, p = .019). No differences in handling time between the first and the sixth 1.5-mm D. Umgispinawere observable with the two sizes of stickleback. We used the original notes by Nuutinen and Ranta (1986) to score handling times for the first and the eighth prey eaten by adult female smooth newts. The handling time was defined as beginning with a successful strike and ending when the newt's characteristic chewing and swallowing movements stopped (Nuutinen and Ranta, 1986). The newts were deprived of food for 12 h before the start of the experiments. With 2.7-mm D. magna, handling times of the first prey item average 6.0 s (SE = 0.7) and of the eighth item 9.5 s (SE = 0.8). A paired t test indicates that the difference is statistically significant (tg = 3.61, p = .006). No such change was observed with 1.7-mm D. magna. Obviously, handling of the larger prey cannot increase ad infinitum. We propose that the handling time counter is reset (e.g., when the gut contents are digested). Foraging strategies In this section we describe properties of three different preyselection strategies and their predictions about diet dynamics during a foraging bout in a patch with two prey types. We dien compare performance of these strategies in terms of energy intake and diet dynamics over simulated foraging bouts. Predators using any of these strategies are assumed to make prey-choice decisions that maximize the amount of energy gained in foraging time. The differences in some of the as- Handling time as a function of the sequence number of prey eaten by F-2 larvae of the odonate Acshna juncta. Three different prey sizes are graphed separately, (a) 1.7-mm, (b) 2.7-mm, and (c) 3.8-mm D. magna. The insets give the regression line y = a + bx parameters (indicated with broken line whenever the slope, b, deviates from zero), together with the Pearson correlation coefficient, r. sumptions and properties of the strategies lead to divergent results in foraging performance. Fixed strategy Consider, according to the classical prey-choice model (e.g., Stephens and Krebs, 1986), a predator living in an environment with two prey types, with net energy values e, and e%, encountered at rates X, and X2 per unit time during a total time, T, spent foraging. We assume diat «, and ^ already include the energetic cost the forager pays for handling these prey types. The handling times for the two prey types are A, and Aj, respectively. The profitabilities (<i/A, > <^/Aj) describe the ratios of energy gained per attack to the handling time per attack by the predator while eating either of the two prey types. The overall rate of net energy intake of an unselective predator is (1) T 1 + X,A, + which for an energy maximizer says that specialization in prey type 1 pays if 497 Hirvonen and Rania • Diet dynamics X, (2) «; That is, the energy gain per foraging time is maximized when the rate of net energy gain from the more profitable prey type alone is greater than that derived by eating both prey types. Equation 2 gives, in terms of time to find the next prey item of type 1, a threshold value for specialization. A forager adopting this strategy would behave in accordance with the classical prey model (Table 1), obeying Equation 2, and hence maximizing the long-term average rate of energy intake during foraging (Charnov, 1976; Gilliam et al., 1982; Stephens and Charnov, 1982; Stephens and Krebs, 1986). The only factor the predator can control is whether to attack an item of prey type i (Charnov, 1976). The classical prey-choice model (Table 1) assumes that a forager following a decision policy according to Equation 2 should not take into account the actual changes in prey profitability during foraging. In other words, this forager uses the handling time of the first prey of each prey type as an estimate of prey handling time over the bout. Everything else being equal, a forager adopting this strategy should not change its selectivity over the bout, and fixed diet choice is predicted. We call this strategy ERIC. Strategy using acquired information Modeling the strategy using acquired information is based on the properties of the classical prey model. However, changes in handling time, as observed in real foraging events, are now included. To formulate a model of prey choice according to the observations on variable handling time supposes that some of the assumptions of the classical prey model (cf. Table 1) have to be modified. First, handling time of a given prey type is allowed to change as a function of the number of this prey type eaten. Second, predators can use the information they gather from their own performance and act on the consequences for prey profitability in the course of foraging. With these modifications, analogically to Equation 2, the rule for specialization of this strategy, ELMO, is 1 < _ MB|)> (3) relative prey profitability) in the course of foraging. It will use this information to decide whether to attack a prey upon encountering it or wait for the next prey in order to maximize the net amount of energy gained in the total time spent foraging. Suppose the forager is about to feed on an encountered prey, knowing its handling time and the time to the next prey it would encounter. The predator using ALEX can either skip the current prey or capture and eat it When doing the latter, the forager pays the cost of losing the next prey item it may encounter if it were not engaged in handling the current one, provided the handling time of the current prey is longer than the time to encounter the next item. That is, because the predator is handling the current prey, the predator does not have the option of capturing the new prey encountered. Foraging by ALEX can be seen as a decision tree (e.g., French, 1989; Taha, 1992). Upon encounter of the first prey, the forager can either accept the prey item or reject it When rejecting, the time to the next branching point is the time to the next encounter. With this second prey a new accept/reject decision is made. However, if the forager decides to accept the first prey encountered, the length of the next branch is the time to the next entry of a prey in the predator's reactive field only if this time is longer than the handling time of the current prey. If one or more prey items enter the reactive field while the predator is still handling the current prey, these new items will be lost. Then the branch length extends to the time of the first encounter after handling of the current prey has terminated. The next decision is then based on the updated handling time of the prey type last eaten. Since the first encounter the forager has a large number of branching decisions to be made. The best sequence of decisions is the one yielding the highest energy gain during the entire foraging time. We assume ALEX can compare the alternatives with true parameters of each prey item to make these decisions. The strategy ALEX was implemented by using the dynamic modeling principles in decision analysis (e.g., French, 1989). Note that ALEX is not a stochastic dynamic programming model (e.g., Godin, 1990; Hart, 1994; Hart and Gill, 1993; Mangel and Clark, 1988), but a dynamic decision model (French, 1989; Taha, 1992). X, where /»,(n,) indicates that handling time for prey type i is a function of its sequence number eaten. For example, the function h,(n,) can be a linear equation (Figure 2), where the constant (plus slope) is the handling time for the first prey and the slope is the increase of handling time with subsequent prey items of this type eaten. The strategy ELMO satisfies the rule set by Equation 3, which is a logical extension of Equation 2. If, as was shown above, the handling time for the initially more profitable prey type, A,, increases with the number of this prey type eaten, n,, within a bout, the value of the right-hand side of Equation 3 decreases. If the encounter rate, X,, for the prey type 1 does not increase, at some n, it is energetically more rewarding for the predator to eat both prey types indiscriminately. This is because updating handling times of the two prey types according to their number eaten continuously updates the threshold value in Equation 3. A separate counter runs for both prey types. Dynamic decision strategy using acquired information The forager using this strategy, ALEX, is assumed to be a truly omniscient predator and thus to have complete information on type, encounter rate, and handling time for each prey item it will encounter during a foraging bout. Note that a predator adopting the ALEX strategy takes into account the possible changes in handling time (and consequently the changes in Simulations We examined the overall performance of the foraging strategies (ERIC, ELMO, ALEX) with simulations. In our simulations, two prey types (X, = 0.4, e, = 6, A, = 2, and X2 = 0.25, «2 = 1 and A, = 1; with these realistic average values, the inequality of Equation 2 of the classical prey' model holds) were randomly allocated (using the X,) over a foraging period of 200 time units. The performance of the three strategies in terms of cumulative energy gain and dynamics of diet choice during the foraging time were tested in this prey environment. RESULTS When the handling time for the prey type 1 is not allowed to change through the foraging time (increase in A, with prey sequence is 0%), the three strategies fare equally well (Figure 3). However, including lengthening of the handling time for the prey type 1 as a function of the number of prey of that type eaten gradually devalues the profitability of this prey type. As the predator using the dynamic decision strategy ALEX knows the properties of the prey item it has just encountered and those of the prey it would encounter while handling the first one (if it is more profitable to take that one than to wait for the next one), it always gains more than predators adopting either of the two other strategies. The strategy ELMO, which takes into account the changes in handling time, gives a some- Behavioral Ecology Vol. 7 No. 4 498 100 0%, 120 Eric. Elmo 80 60 40 ulativega 20 Figure 3 Simulated examples of cumulative energy gain as a function of elapsing foraging time for the three different prey-choice strategies (ALEX, ELMO, ERIC; see text for details). The percentages give the rate of increase in handling time of the prey type 1 as a function of the number of this prey type eaten. Handling time of prey type 2 is constant. The maximum cumulative energy gain by the three strategies is indicated by italic numbers (ALEX, ELMO, and ERIC are scaled to this value). E d 0 100 80 60 40 20 0 0 50 100 150 200 50 100 150 200 Time what higher cumulative energetic gain than the fixed strategy, ERIC (Figure 3). This is because, at a given point, according to Equation 3, diet specialization no more pays for the ELMO predator adjusting its selectivity as relative prey profitabilities change, and it shifts to eating the two prey types indiscriminately. From the shifting point onward, this strategy gives a higher rate of intake than sticking to the fixed choice. Note that for all the three strategies, the rate of intake declines as handling time for the prey type 1 increases (Figure 3). To examine the dynamics of prey selection, we again split the foraging bout into two halves according to the median prey eaten. The proportion of the prey type 2 in die predator's diet in both halves was then scored for the adjusted selectivity strategy, ELMO, and for the dynamic decision strateTable 3 Diet dynamics of two foraging strategies (ELMO, ALEX) over simulated (100 simulations) foraging bouts 5% gy, ALEX. Recall that according to Equation 2, no changes in prey selection of the forager adopting thefixedstrategy, ERIC, are expected. We used the same parameter values reported above in the description of the simulations for energy intake. For each combination the simulations were run 100 times. When the handling times are constant, the adjusted strategy (ELMO) is specializing in the better prey type over the trial (Table 3). As handling time for the prey type 1 increases with consecutive feeds of this prey type, the predator using the ELMO strategy will switch from a diet specialist to a diet generalist during the foraging bout, and the proportion of the small prey in its diet increases in the second half of the bout (Table 3). As the increase in handling time steepens, the shifting point moves toward the beginning of the bout, and the difference in diet composition between the two halves eventually vanishes (Table 3). The dynamic decision strategy, ALEX, on the other hand, shows no change in diet, irrespective of the slope of increase in hx (Table 3). DISCUSSION Lengthening of A, with n, 0% 0 15% 10% Behavioral mechanisms of diet dynamics Strategy 1st half 2nd half 1st half 2nd half 1st half 2nd half 1st half 2nd half ELMO ALEX 0 52 0 53 5 53 35 54 23 54 40 53 30 56 36 53 The figures are average proportions (%) of the smaller (initial!)' less profitable) prey type in the forager diets in the first and the second half of the prey eaten during the bouts. Results are from simulations with four different slopes (%) of increase in handling time, A], of the large (initially more profitable) prey type as a function of prey sequence, n, (see text for details). We found that all the four small aquatic predator species changed their diet toward the end of the foraging bout by including more of the initially less profitable prey type. These observations are consistent with those of Confer and O'Bryan (1989) on small rainbow trout (Oncorhyncus irtykiss) and yellow perch (Percaflavescens)feeding on zooplankton. As our simulations demonstrated, within-bout broadening of the diet was only predicted by the strategy ELMO, in which prey choice was based on updated prey profitabilities. The truly omniscient strategy (ALEX), also using the knowledge of the changes in handling time, did not show shifts in prey selection 499 Hirvonen and Ranta • Diet dynamics because it could anticipate the forthcoming prey and therefore could choose the ideal composition of prey items from those it would encounter during the foraging period. For a real predator, this is hardly possible. Thus, our results suggest that predators reevaluate profitabilities of prey types during foraging and adjust their prey choice accordingly. This conclusion is substantiated by experimental evidence that shows animals can assess parameters included in foraging models (e.g., Charnov, 1976; Jaeger et al., 1982; Shetdeworth and Plowright, 1992; Stephens et al., 1986). In addition, foragers are clearly capable of updating their diet-choice decisions (Cudiill et al., 1990), even over surprisingly short time scales (Jaeger et al., 1982; Lucas, 1987b, 1990). We suppose that widiin-bout changes in relative prey profitability and in diet choice are rather general, but they have often been overlooked. Many foraging studies on planktivorous fish, for example, have used die first short (< 2 min) feeding bursts to rank prey and/or test prey preference (e.g., Bence and Murdoch, 1986; Buder and Bence, 1984; Li et al., 1985; Werner and Hall, 1974; but see Confer and O'Bryan, 1989, for an exception). Disregarding widiin-bout changes in foraging could have been due to, among other things, clinging tighdy to the classical prey model. Experiments testing the predictions of die classical model have often been of relatively short duration, and thus changes in diet composition due to increased handling time, for example, could have been unnoticed. For example, Krebs et al. (1977) truncated die data on die foraging trials widi great tits after 10 prey items were eaten (< 300 s) because handling time of die large prey tended to increase after diat and dierefore would have violated one basic assumption of die classical prey-choice model. If foragers change dieir selectivity during foraging, as we have demonstrated, pooling data on prey selection over foraging time may show apparent partial preferences, as has been demonstrated in odier empirical (Godin, 1990) and dieoretical (Lucas, 1983, 1985; Lucas and Schmid-Hempel, 1988) examinations. Thus, widiin-bout dynamics of diet selection could in part explain why partial preferences are so often observed in studies on prey choice (Krebs and McCleery, 1984; McNamara and Houston, 1987; Stephens and Krebs, 1986). A variety of alternative foraging models have been used to predict dynamics in diet selection. However, a common property of diese models is diat die predictions only apply in certain conditions defined by tight assumptions. For example, foraging under time constraints has been suggested to prompt die forager to switch from a specialist to a generalist diet at die end of die bout (Lucas, 1987a,b; Yoerg and Kamil, 1988), but only if animals are trained to predict die bout lengdi (Lucas, 1990). Lucas and Schmid-Hempel (1988) showed diat diet widdi should increase with die time die forager has been in a depleting patch, whereas in nondepleting patches, diet widdi should decrease widi decreasing time left in die patch. Some theoretical explorations and empirical tests suggest that diet dynamics is due to changes in a forager's hunger level, but disagree whedier diet widdi should increase (e.g., Barnard and Hurst, 1987; Godin, 1990; Richards, 1983) or decrease (e.g., Hart and Ison, 1991; Lucas et al., 1993; Schoener, 1971; Snyderman, 1983) widi satiation. It follows diat die direction of die change in selectivity during a foraging bout cannot be derived on die mere basis of satiation. In addition to satiation, prey size relative to predator size and die internal state of die predator may be important factors in determining prey choice (Hart, 1994; Hart and Gill, 1993). Furthermore, according to die prediction of die modified model, ELMO, die direction of die switch in diet would depend on die actual relative profitabilities of die given prey types, not on satiation as such. Following Pulliam's idea (Pulliam, 1974), alterations in diet choice have recendy been explained by models based on state- dependent decisions of animals balancing energy intake and odier demands (Godin, 1990; Hart, 1994; Houston, 1993; Houston and McNamara, 1985; Sih, 1993). If diet-choice decisions affect die risk of predation, foragers should take more risks when hungry, but choose less risky options as diey near satiation (McNamara, 1990). For example, diet width of die guppies studied by Godin (1990) increased widi duration of die foraging bout Large Daphnia, which took longer to handle, were preferred at die beginning of die foraging trials, but as more prey were eaten, die guppies shifted dieir diet, and die diree prey types became equally likely to be eaten. The result is in accordance widi our observations. [According to Godin (Godin J-GJ, personal communication), handling times of large- and medium-sized prey tended to increase widi increasing number of prey ingested during die foraging bouts, dius matching our observations.] Godin (1990), however, suggested die change in die guppies' diet to be a consequence of a state-dependent shift in the optimization criterion from energy maximization to minimization of predation risk, diough no predators were present In contrast to state-dependent models, our modified model (ELMO) demonstrates diat in many situations no change in die assumptions of optimization currency is required to explain dynamics of optimal diets. Variable handling time and prey choice Our findings support die reports suggesting diat lengdiening of handling time is more pronounced as prey size increases in relation to predator size (Bindoo and Aravindan, 1992; Kislalioglu and Gibson, 1976; Krebs et al., 1977; Smidi and Dawkins, 1971). This would cause a gradual decline in profitability of die larger prey. Because handling time did not seem to be under die foragers' control, we assumed it as a constraint The exact mechanism causing die increase in handling time in die course of foraging is not known. It has often been related to satiation effects, but our results indicate diat satiation alone cannot account for diis phenomenon. However, die interpretation depends on how satiation is defined. For example, widi die odonates handling time for die large Daphnia increases after only a few items have been eaten, aldiough die predator was prone to eat a much larger number of prey (see Figure 2). Similarly, for die large ten-spined sticklebacks, it took double die time to handle die sixth large Daphnia compared to die first one, diough sticklebacks are capable of eating many more prey (Ranta and Nuutinen, 1984). The same holds for die smooth newt (Nuutinen and Ranta, 1986; Ranta and Nuutinen, 1985). Thus, it seems diat handling times for die large prey started to increase when die foragers had eaten only a negligible portion of dieir capacity. Our findings are supported by Confer and O'Bryan (1989), who reported diat small rainbow trout switched prey preference when dieir guts were about 9%-25% full. Similarly, Lucas (1987a) found diat diet shift of great tits widiin die foraging bout was unlikely to be due to satiation effects. Furthermore, odier evidence indicates diat large prey could be more difficult to process and ingest dian small prey (Bence and Murdoch, 1986; Confer and O'Bryan, 1989; Ernsting and van der Werf, 1988; Kislalioglu and Gibson, 1976). The lengdiening of handling time and its dependence on prey size could also relate to feedback mechanisms from the gut (Johnson et al., 1975) or to stomach packing and gut fullness (Hart and Gill, 1992). Regardless of die underlying mechanisms, change in handling time of a prey type has obvious consequences on diet choice. By specifying die assumptions of die classical preychoice model and re-forming it by incorporating changes in prey profitability widiin die foraging bout, we could better predict how die predators choose dieir diet 500 We thank Jean-Guy Godin for discussions on the topic and for providing us with unpublished information of his experiments on the diet of the guppy. Comments by Veijo Kaitala, Anssi Laurila, Nina Peuhkuri, Paul Schmid-Hempel, and anonymous referees on earlier drafts helped us to improve this paper. We also thank David Stephens for discussions and appreciate Alejandro Kacelnik's comments and advice. The experimental work was done at the Tvarminne Zoological Station, University of Helsinki. The study was supported by the Academy of Finland and the Finnish Cultural Foundation. REFERENCES Barnard CJ, Hurst JL, 1987. Time constraints and prey selection in common shrews Sorex ara-ncus L. Anim Behav 35:1827-1837. Bence JR, Murdoch WW, 1986. Prey size selection by the mosquitofish: relation to optimal diet theory. Ecology 67:324-336. Bindoo M, Aravindan CM, 1992 Influence of size and level of satiation on prey handling time in Channa stnata (Bloch). J Fish Biol 40:497-502. Butler W, Bence JR, 1984. A diet model for planktivores that follow density-dependent rules for prey selection. Ecology 65:1885—1894. Charnov EL, 1976. Optimal foraging: attack strategy of a mantid. Am Nat 110:141-151. Confer JL, O'Bryan LM, 1989. Changes in prey rank and preference by young planku'vores for short-term and long-term ingestion periods. Can J Fish Aquat Sci 46:1026-1032. Croy MI, Hughes RN, 1991. The role of learning and memory in the feeding behaviour of fifteen-spined stickleback, Spinachia spinachia L. Anim Behav 41:149-159. Cuthill IC, Kacelnik A, Krebs JR, Haccou P, Iwasa Y, 1990. Patch use by starlings: the effect of recent experience on foraging decisions. Anim Behav 40:625-640. Emlen JM, 1966. The role of time and energy in food preference. Am Nat 100:611-617. Emlen JM, 1973. Ecology: an evolutionary approach. New York: Addison-Wesley. Ernsting G, van der Werf DC, 1988. Hunger, partial consumption of prey and prey size preference in a carabid beetle. Ecol Entomol 13: 155-164. French S, 1989. Readings in decision analysis. London: Chapman Hall. Gilliam JF, Green RF, Pearson NE, 1982. The fallacy of traffic policeman: a response to Templeton and Lawlor. Am Nat 119:875-878. Godin J-GJ, 1990. Diet selection under the risk of predation. In: Behavioural mechanisms of food selection. NATO ASI Series, vol. G 20 (Hughes RN, ed). Berlin: Springer-Verlag; 739-769. Hart PJB, 1994. Theoretical reflections on the growth of three-spined stickleback morphs from island lakes. J Fish Biol 45(suppl. A):27-40. Hart PJB, Gill AB, 1992. Constraints on prey size selection by the three-spined stickleback: energy requirements and the capacity and fullness of the guLj Fish Biol 40:205-218. Hart PJB, Gill AB, 1993. Choosing prey size: a comparison of static and dynamic models for predicting prey choice by fish. Mar Behav Physiol 23:91-104. Hart PJB, Ison S, 1991. The influence of prey size and abundance, and individual phenotype on prey choice by the three-spined stickleback, Gasterosteus aculealus L. J Fish Biol 38:359-372. Holling CS, 1959. Some characteristics of simple types of predation and parasitism Can Entomol 91:385-398. Houston A, 1993. The importance of state. In: Diet selection. An interdisciplinary approach to foraging behaviour (Hughes RN, ed). Oxford: Blackwell; 10-31. Houston A, McNamara J, 1985. The choice of two prey types that minimises the probability of starvation. Behav Ecol Sociobiol 17: 135-141. Jaeger RG, Barnard DE, Joseph RG, 1982. Foraging tactics of a terrestrial salamander: assessing prey density. Am Nat 119:885—890. Johnson DM, Akre BG, Crowley PH, 1975. Modeling arthropod predation: wasteful killing by damselfly naiads. Ecology 56:1081-1093. Kislalioglu M, Gibson RN, 1976. Prey 'handling time' and its importance in food selection by the fifteen-spined stickleback, Spinachia spinarhia (L.). J Exp Mar Biol Ecol 25:151-158. Krebs JR, Erichsen JT, Webber MI, 1977. Optimal prey selection in the great tit (Parus major). Anim Behav 25:30-38. Behavioral Ecology Vol. 7 No. 4 Krebs JR, Kacelnik A, 1991. Decision-making. In: Behavioural ecology, 3rd ed (Krebs JR, Davies NB, eds). Oxford: Blackwell; 105-136. Krebs JR, McCleery R, 1984. Optimization in behavioural ecology. In: Behavioural ecology, 2nd ed (Krebs JR, Davies NB, eds). Oxford: Blackwell; 91-121. Krebs JR, Stephens DW, Sutherland WJ, 1983. Perspectives in optimal foraging. In: Perspectives in ornithology (Brush AH, Clark GA, eds). New York: Cambridge University Press; 165-216. Krebs JR,et al., 1977 Li KT, WettererJK, Hairston Jr NG, 1985. Fish size, visual resolution and prey selectivity. Ecology 66:1729-1735. Lucas JR, 1983. The role of foraging time constraints and variable prey encounter in optimal diet choice. Am Nat 122:191-209. Lucas JR, 1985. Time constraints and diet choice: different predictions from different constraints. Am Nat 126:680-705. Lucas JR, 1987a. Foraging ume constraints and diet choice. In: Foraging behavior (Kamil AC, Krebs JR, Pulliam HR, eds). New York: Plenum Press; 239-269. Lucas JR, 1987b. The influence of time constraints on diet choice of the great tit, Parus major. Anim Behav 35:1538-1548. Lucas JR, 1990. Time scale and diet choice decisions. In: Behavioural mechanisms of food selection. NATO ASI Series, vol. G 20 (Hughes RN, ed). Berlin: Springer-Verlag; 165-184. Lucas JR, Peterson LJ, Boudinier RL, 1993. The effects of time constraints and changes in body mass and satiation on the simultaneous expression of caching and diet-choice decisions. Anim Behav 45: 639-658. Lucas JR, Schmid-Hempel P, 1988. Diet choice in patches: time constraint and state-space solutions. J Theor Biol 131:307-332. MacArthur RH, Pianka ER, 1966. On the optimal use of a patchy environment Am Nat 100:603-609. Mangel M, Clark CW, 1988. Dynamic modeling in behavioral ecology. Princeton, New Jersey. Princeton University Press. McNamara JM, 1990. The starvation-predauon trade-off and some behavioural and ecological consequences. In: Behavioural mechanisms of food selection. NATO ASI Series, vol. G 20 (Hughes RN, ed). Berlin: Springer-Verlag; 39-58. McNamara JM, Houston AI, 1987. Partial preferences and foraging Anim Behav 35:1084-1099. Nuutinen V, Ranui E, 1986. Size-selective predation on zooplankton by the smooth newt, Triturus vulgaris. Oikos 47:83—91. Pulliam HR, 1974. On die theory of optimal diets. Am Nat 108:59-75. Ranta E, Nuutinen V, 1984. Zooplankton predation by rock-pool fish (Tinea tinea L. and Pungiiius pungitius L.): an experimental study. Ann Zool Fenn 21:441-449. Ranta E, Nuutinen V, 1985. Foraging by the smooth newt (Triturus vulgaris) on zooplankton: functional responses and diet choice. J Anim Ecol 54:275-294. Richards LJ, 1983. Hunger and the optimal diet Am Nat 122:326-334. Schoener TW, 1971. Theory of feeding strategies. Annu Rev Ecol Syst 11:369-404. Shettleworth SJ, Plowright CMS, 1992. How pigeons estimate rates of prey encounter. J Exp Psychol Anim Behav Procs 18:219—235. Sih A, 1993. Effects of ecological interactions on forager diets: competition, predation risk, parasiusm and prey behaviour. In: Diet selection. An interdisciplinary approach to foraging behaviour (Hughes RN, ed). Oxford: Blackwell; 182-211. Smith JNM, Dawkins R, 1971. The hunting behaviour of individual great tits in relation to spatial variations in their food density'. Anim Behav 19:695-706. Snyderman M, 1983. Optimal prey selection: the effects of food deprivation. Behav Anal Letts 3:359-369. Stephens DW, Charnov EL, 1982. Optimal foraging: some simple stochastic models. Behav Ecol Sociobiol 10:251-263. Stephens DW, KrebsJR, 1986. Foraging theory. Princeton, New Jersey: Princeton University Press. Stephens DW, Lynch JF, Sorensen AE, Gordon C, 1986. Preference and profitability: dieory and experiment Am Nat 127:533—553. Taha HA, 1992. Operations research. London: Prentice Hall International. Werner EE, DJ Hall, 1974. Optimal foraging and the size selection of prey by die bluegill sunfish (Lepomis macrochirus). Ecology 55: 1042-1052. Yoerg SI, Kamil AC, 1988. Diet choices of blue yum (Cyanocitta mslata) as a function of time spent foraging. J Comp Psychol 102:230-235.
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